Earaches and outer ear infections are commonly associated with swimming. In this study, we estimated the excess risk and health burden of earaches due to swimming in natural fresh and marine waters using results from a survey of over 50,000 beachgoers at nine beaches across the United States.
Prospective cohort studies were conducted at four freshwater and five marine sites in the United States and Puerto Rico. Beach visitors were enrolled on summer weekends and holidays. Ten to twelve days after the beach visit, respondents answered questions about health symptoms, including earaches or ear infections experienced since the beach visit. Economic and physical burdens were also obtained. Fixed slope, random intercept (beach site) multivariate logistic regression models were used to estimate the relationship between head immersion swimming exposure and earaches. Model results were used to calculate excess risk for earaches attributable to swimming.
The overall incidence of self-reported earache was 1.6% in the 10–12 days after the beach visit. Earaches were more frequent in head immersion swimmers compared to non-swimmers for all beach sites and age groups. Earaches were unassociated with water sample measures of fecal contamination and turbidity. After adjustment for covariates, we calculated 7.12 excess earaches among head immersion swimmers per 1,000 swimming events. Twenty-four percent of those with earache reported missing their regular activities; 28% visited a doctor; 4% visited the emergency room; and 31% and 40% used prescription and non-prescription medications, respectively.
There are at least 128 million swimming events in natural waters annually. Such frequent exposures could result in 900,000 excess earaches, 260,000 visits to the doctor, 39,900 visits to the emergency room, nearly $4 million dollars in out-of-pocket expenditures on prescription and over-the-counter medications, and close to 75,000 hours of clinician time. More accurate estimates of swimming exposure are needed to improve population burden and associated cost estimates.
Ear pain (otalgia) is one of the most common reasons for visits to primary care physicians and medical care providers
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The health-care burden associated with earaches and ear infections is considerable. An estimated 2.4 million U.S. health-care visits (8.1 visits per 1,000 population) were associated with a diagnosis of acute otitis externa (ambulatory care or emergency room) in 2007
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The data used for this analysis were obtained from interviews of beach goers at the nine beach sites studied as part of the NEEAR Water Study. The first phase focused on beaches in temperate climates, located near one or more treated sewage discharge points. Four freshwater beach sites located in the Great Lakes (Lake Michigan and Erie) were studied in 2003 and 2004
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The study design, subject recruitment and questionnaire administration have been described previously
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All study participants provided verbal consent. The study design, procedures and protocols were approved by the Institutional Review Boards for the Centers for Disease Control and Prevention and the University of North Carolina.
At the telephone interview, respondents were asked if they had “an earache, ear infection or runny ears” since the beach interview (referred to as “earache”). Participants reporting earache were also asked when the symptoms started and for how many days they lasted. They were also asked whether they or others lost time from work or regular activities, consulted a health care provider, visited an emergency room, were admitted to the hospital, and/or used prescription or over the counter medications as a result of the earache.
Participants who reported having an earache, ear infection or runny ears in the three days prior to the beach interview were considered prevalent cases and excluded from the analysis. Those who reported that their ear associated symptoms were due to allergies were also excluded.
Because moisture in the ear is an important factor for swimming-related ear infections, head immersion or submersion in water was the primary exposure of interest. Three mutually exclusive exposure categories were generated: 1) Head immersion swimmers (“Swimmers”), were participants who reported submerging their head or putting their face in water; 2) Non-swimmers were those who reported no water contact; and 3) “Waders” were those who swam but did not immerse their head. Non-swimmers were used as the reference group for risk calculations.
Earache (presence or absence) was the health outcome of interest and head immersion swimming was the primary exposure. Incidence of earache was tabulated and summarized by demographic characteristics, beach activities, and environmental exposures. Logistic regression models including a random intercept for beach site, were used to estimate the association between swimming and incidence of earache. Initial models included age category, race, sex, regular frequency of visits to the beach, miles traveled to the beach, burying body in sand, precipitation in the previous 17 hours, contact with unfamiliar animals, other swimming exposures, use of sunblock, use of insect repellent, use of ear plugs, presence of allergies, asthma, or chronic skin conditions and number of other beachgoers in the water. Final models were selected by sequentially removing variables from the full model (backward selection), minimizing Akaike’s Information Criterion (AIC)
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Following final model selection, the excess risk (ER) associated with swimming, adjusted for covariates, was determined using “G-computation”
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where n is the total number of observations (subjects);
To develop estimates of the impacts of earache on cost, personal time and health care utilization, the following responses were tabulated and summarized among those reporting earache: missing regular activities, others missing regular activities, phoning a doctor or nurse, visiting a doctor or nurse, visiting the emergency room, using prescription medicines, and using over-the-counter medications. The percentages of all respondents reporting these impacts were assumed to apply to the fraction of swimming-associated earache and were used as multipliers to attribute the health impact due to swimming:
where
Survey data was collected on a total of 54,250 respondents. Excluding those with earache at baseline (N = 717), those with missing responses for earache (N = 176), and earaches due to allergy (N = 95), the overall incidence of earache was 1.6% (N = 829/53,262) in the 10–12 day follow up period. Descriptive and demographic characteristics for these subjects are shown in Table
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| 1 and under | 1058 | 97.6 | 26 | 2.4 | 1084 | 100.0 |
| 2–5 | 3478 | 98.0 | 70 | 2.0 | 3548 | 100.0 |
| 6–10 | 4819 | 97.7 | 111 | 2.3 | 4930 | 100.0 |
| 11–19 | 7839 | 98.4 | 125 | 1.6 | 7964 | 100.0 |
| 20–50 | 26723 | 98.5 | 407 | 1.5 | 27130 | 100.0 |
| Over 50 | 7586 | 99.0 | 80 | 1.0 | 7666 | 100.0 |
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| Male | 23289 | 98.6 | 333 | 1.4 | 23622 | 100.0 |
| Female | 29037 | 98.3 | 493 | 1.7 | 29530 | 100.0 |
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| Non-white | 21060 | 98.4 | 337 | 1.6 | 21397 | 100.0 |
| White | 31241 | 98.5 | 489 | 1.5 | 31730 | 100.0 |
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| No contact | 14037 | 99.0 | 144 | 1.0 | 14181 | 100.0 |
| Contact withouthead immersion | 13351 | 98.7 | 179 | 1.3 | 13530 | 100.0 |
| Head immersion | 24736 | 98.0 | 501 | 2.0 | 25237 | 100.0 |
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| No | 48059 | 98.5 | 727 | 1.5 | 48786 | 100.0 |
| Yes | 4371 | 97.7 | 102 | 2.3 | 4473 | 100.0 |
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| No | 19195 | 98.7 | 250 | 1.3 | 19445 | 100.0 |
| Yes | 32964 | 98.3 | 573 | 1.7 | 33537 | 100.0 |
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| No | 47355 | 98.5 | 723 | 1.5 | 48078 | 100.0 |
| Yes | 4824 | 97.9 | 101 | 2.1 | 4925 | 100.0 |
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| No | 48615 | 98.5 | 733 | 1.5 | 49348 | 100.0 |
| Yes | 3786 | 97.5 | 96 | 2.5 | 3882 | 100.0 |
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| No | 49942 | 98.5 | 780 | 1.5 | 50722 | 100.0 |
| Yes | 2454 | 98.0 | 49 | 2.0 | 2503 | 100.0 |
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| No | 43808 | 98.6 | 635 | 1.4 | 44443 | 100.0 |
| Yes | 8569 | 97.8 | 194 | 2.2 | 8763 | 100.0 |
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| No | 51781 | 98.4 | 816 | 1.6 | 52597 | 100.0 |
| Yes | 568 | 97.8 | 13 | 2.2 | 581 | 100.0 |
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| No | 35708 | 98.8 | 449 | 1.2 | 36157 | 100.0 |
| Yes | 16648 | 97.8 | 379 | 2.2 | 17027 | 100.0 |
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| Fresh | 20437 | 98.7 | 267 | 1.3 | 20704 | 100.0 |
| Marine | 31996 | 98.3 | 562 | 1.7 | 32558 | 100.0 |
1Including waders, excluding those with earache at baseline and earache due to allergy (N = 53,262).
2Categories may not add to 53,262 due to missing values.
3Other head immersion swimming in the 1-week prior to the beach visit.
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| 1 and under | 355 | 48.1 | 383 | 51.9 | 738 | 100.0 |
| 2–5 | 379 | 14.8 | 2185 | 85.2 | 2564 | 100.0 |
| 6–10 | 340 | 8.1 | 3864 | 91.9 | 4204 | 100.0 |
| 11–19 | 1448 | 21.8 | 5193 | 78.2 | 6641 | 100.0 |
| 20–50 | 8265 | 43.0 | 10970 | 57.0 | 19235 | 100.0 |
| Over 50 | 3188 | 59.6 | 2158 | 40.4 | 5346 | 100.0 |
| Total | 13975 | 36.1 | 24753 | 63.9 | 38728 | 100.0 |
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| Boquerón, PR | 2915 | 22.8 | 9878 | 77.2 | 12793 | 100.0 |
| Edgewater, AL | 370 | 46.8 | 421 | 53.2 | 791 | 100.0 |
| Fairhope, MI | 834 | 56.8 | 634 | 43.2 | 1468 | 100.0 |
| Goddard, RI | 1558 | 66.9 | 772 | 33.1 | 2330 | 100.0 |
| Huntington, OH | 1513 | 74.9 | 506 | 25.1 | 2019 | 100.0 |
| Surfside, SC | 1722 | 21.5 | 6274 | 78.5 | 7996 | 100.0 |
| Silver, MI | 3324 | 46.1 | 3881 | 53.9 | 7205 | 100.0 |
| West, IN | 708 | 37.2 | 1197 | 62.8 | 1905 | 100.0 |
| Washington Park, IN | 1237 | 42.5 | 1674 | 57.5 | 2911 | 100.0 |
| Total | 14181 | 36.0 | 25237 | 64.0 | 39418 | 100.0 |
1Excluding waders, those with earache at baseline, earache due to allergy and those with missing data on earache at follow up.
2Categories for age do not add to 39,418 due to missing values.
The incidence of earache for swimmers and non-swimmers by age category and beach site are shown in Figures
Earache incidence among swimmers was not associated with the level of fecal contamination as measured by
Among swimmers, increasing time spent in water was not associated with an increase in the incidence of earache (p = 0.30). Those spending more than two hours reported earaches at the approximately same frequency as those spending 15 minutes or less in the water (2.0% vs 1.8%, respectively).
Adjusted estimates from fixed slope random-intercept logistic regression models are shown in Table
Adjusted odds ratios for earache at marine and fresh water sites
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| Head immersion swimming | 1.67**** | 1.35,2.07 | 1.56*** | 1.21,2.00 | 2.10**** | 1.48,2.99 | |||||||
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| Age 0–1 | 2.02** | 1.28,3.21 | 1.55 | 0.84,2.88 | 3.00** | 1.48,6.07 | |||||||
| Age 2–5 | 1.13 | 0.83,1.53 | 1.29 | 0.90,1.84 | 0.79 | 0.45,1.39 | |||||||
| Age 6–10 | 1.27* | 1.00,1.61 | 1.41* | 1.07,1.87 | 0.94 | 0.61,1.45 | |||||||
| Age 11–19 | 0.88 | 0.70,1.11 | 1.00 | 0.77,1.31 | 0.61* | 0.39,0.96 | |||||||
| Over 60 | 0.76+ | 0.57,1.01 | 0.82 | 0.59,1.13 | 0.52+ | 0.25,1.07 | |||||||
| Non-white race | 1.24 | 0.95,1.62 | 1.33** | 1.08,1.63 | 1.11 | 0.73,1.68 | |||||||
| Female | 1.29** | 1.10,1.52 | 1.27* | 1.06,1.54 | 1.35+ | 1.00,1.83 | |||||||
| Unfamiliar animal contact | 1.57*** | 1.23,2.00 | 1.72*** | 1.28,2.31 | 1.31 | 0.86,2.00 | |||||||
| Other swimming1 | 1.60**** | 1.36,1.89 | 1.61**** | 1.33,1.96 | 1.58** | 1.16,2.16 | |||||||
| Used insect repellent | 1.41** | 1.09,1.81 | 1.44** | 1.11,1.88 | 1.21 | 0.53,2.77 | |||||||
| Allergies | 1.61**** | 1.33,1.95 | 1.76**** | 1.41,2.21 | 1.31 | 0.91,1.88 | |||||||
| Asthma | 1.46** | 1.13,1.87 | 1.38* | 1.03,1.86 | 1.71* | 1.05,2.80 | |||||||
+ p <0.1, ∗ p <0.05, ∗∗ p <0.01, ∗∗∗ p <0.001, ∗∗∗∗ p <0.0001.
AOR = Adjusted Odds Ratio, 95% CI = 95% Confidence Interval.
1Other head immersion swimming in the 1-week prior to the beach visit. Estimates from a logistic regression model with a random intercept for beach.
Because of the frequency of otitis media infections (which are not normally attributed to swimming) among infants and young children, we conducted additional analyses excluding children one year of age and under and five years of age and under. We also examined the association between earache and swimming only among children five and under. Results are provided in the supplement (See Additional file
Models with multiplicative interactions terms between swimming and beach site and age category did not improve the model fit as indicated by the AIC or Likelihood Ratio Test. Because of the consistency of the association between earache and swimming exposure across beaches and age groups, we used models that combined across these factors. We accounted for potential heterogeneity in the effect across beach sites with a random intercept term.
Excess risks for earaches,
Among all subjects, 829 participants reported a new episode of earache (excluding those with earaches due to allergy and those reporting earache at baseline). Percentages of those with earaches who reported an economic or health care impact (
Percentage of respondents with earache (N = 829) reporting missing regular activities, visiting the doctor or using medication
| Missed regular activities | 201 | 24.3 |
| Others missed regular activities | 30 | 3.6 |
| Phoned doctor or nurse | 122 | 14.7 |
| Visited doctor or nurse | 235 | 28.3 |
| Visited ER | 36 | 4.3 |
| Used prescription medication | 257 | 31.0 |
| Used over-the-counter medicine | 337 | 40.6 |
Applying Equation 2, the earache-associated health impacts resulting from swimming exposure are shown in Table
Earaches and earache-associated health impacts due to swimming
| Number of earaches | 7.12 |
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| Missed regular activities | 1.73 |
| Phone doctor or nurse | 1.05 |
| Visit to doctor or nurse | 2.02 |
| Visit to emergency room | 0.31 |
| Use of over-the-counter medication | 2.89 |
| Use of prescription medication | 2.21 |
Data collected from a survey of over 50,000 beachgoers were used to estimate the incidence and burden of earaches resulting from swimming in natural waters. For every 1000 swimming events in natural waters there were slightly more than 7 excess earaches. The effect we observed was relatively constant across beach sites and age groups. Although young children reported a higher overall incidence of earache, the risk associated with swimming exposure was slightly lower than other age groups. This is consistent with the age distribution of otitis externa which affects all age groups
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The health care burden and economic impacts of swimming-associated earaches are substantial. The National Survey on Recreation and the Environment
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The costs for over-the-counter and prescription medications reported by participants are a fraction of the direct health care cost of earache. The average cost of a doctor’s office or emergency room visit for otitis externa (including out-of-pocket and insurer costs for the visit and prescription medication) has been estimated to be $200
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In order to estimate the health burden attributable to swimming-associated earache, we assumed that the health burden and impact of earache for all respondents were representative of the swimming-associated fraction. Although we are unaware of evidence to contradict this assumption, we could not directly evaluate it or confirm it with our data.
This analysis also does not consider swimming in pools, water parks and other chlorinated or treated venues. Although swimmer’s ear is known to be associated with these exposures
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Our results are based on self-report of earache. Due to this limitation, we cannot exclude the possibility that at least some of the risk attributable to swimming exposure was a result of over-reporting of earache among swimmers. Swimmers and non-swimmers were unblinded with regard to the primary exposure of interest, head-immersion swimming, and as a result, it is possible that swimmers over-reported earaches based on this knowledge of exposure, resulting in an overestimate of the true excess risk of earache associated with swimming. However this bias, if present, may not have been strong. Subjects reported on numerous symptoms as part of the NEEAR Water study and earaches were not particularly emphasized in relation to these other symptoms. Swimming and non-swimming respondents were therefore probably unlikely to be abnormally or specifically focused on their earache symptoms. Unlike several other symptoms studied, earache was consistently elevated among swimmers relative to non-swimmers across beach sites and age groups. This consistency of effect was not observed for other non-enteric symptoms, and several showed little association with swimming following adjustment for covariates (respiratory, eye irritations)
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We did not clinically confirm or diagnose any of the self-reported earaches as otitis externa. It is likely that some of the excess earaches were due to trauma or other irritation so we cannot determine the excess risk specifically attributable to otitis externa. Nonetheless, preventative measures can be taken to reduce the risk of ear infections following swimming exposure. Clinical reports recommend the use of earplugs as a preventative measure was well as the use of over-the counter acidifying agents with alcohol or other astringent and drying the ears after swimming with a hair dryer on the lowest setting
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Earaches were associated with swimming, but not water quality as measured by the fecal indicator bacteria
In summary, from an analysis of over 39,000 beachgoers at nine freshwater and marine beach sites there were 7.12 excess earaches for every 1,000 head immersion swimming events. We further estimated that for every 1,000 swimming events there were 1.73 earaches that resulted in missed work or activity; 1 that resulted in a phone call to a doctor; 2 in visits to a doctor and 0.31 in visits to an emergency room. As there are over 128 million swimming events in natural waters annually, the population health burden attributable to swimming-associated earaches is considerable. Improved estimates of swimming in natural waters will provide a more accurate estimate of the health burden of swimming associated earaches and other health effects related to swimming exposures.
AOR: Adjusted odds ratio; ER: Excess risk; ER(E): Excess earaches associated with head immersion swimming; ER(E, I): Excess swimming-associated earaches resulting in a health impact; AIC: Akaike’s Information Criterion; qPCR: Quantitative polymerase chain reaction; CI: Confidence interval; p: p-value; EPA: United States Environmental Protection Agency; CDC: Centers for Disease Control and Prevention.
The authors declare that they have no competing interests.
TW led data analysis, interpretation, and manuscript preparation. ES led data collection. MB developed the study design. SC provided calculations for health burden estimates. AD oversaw all aspects of the study. All authors read and approved the final manuscript.
Supplemental information.
Click here for file
The authors would like to acknowledge Dr. Rebecca Calderon (deceased) for her inspiration, dedication and vision; Westat, Inc. especially Karen Della Torre and Kurt Patrizi; and all field study staff, participants, interviewers, and water sample collectors. The authors would also like to thank Dr. Sharon Nappier, Dr. Reagan Converse and Michele Hlvasa for their review and comments.
The views expressed in this paper are those of the authors and do not necessarily reflect the views or policies of the U.S. Environmental Protection Agency or the Centers for Disease Control and Prevention.